CN106967416B - The preparation method of titanium dioxide nano-particle fluorescence probe for DDT detection - Google Patents
The preparation method of titanium dioxide nano-particle fluorescence probe for DDT detection Download PDFInfo
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- CN106967416B CN106967416B CN201710223056.7A CN201710223056A CN106967416B CN 106967416 B CN106967416 B CN 106967416B CN 201710223056 A CN201710223056 A CN 201710223056A CN 106967416 B CN106967416 B CN 106967416B
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- FPCJKVGGYOAWIZ-UHFFFAOYSA-N butan-1-ol;titanium Chemical compound [Ti].CCCCO.CCCCO.CCCCO.CCCCO FPCJKVGGYOAWIZ-UHFFFAOYSA-N 0.000 claims description 10
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- 231100000350 mutagenesis Toxicity 0.000 description 1
- 239000002077 nanosphere Substances 0.000 description 1
- 239000013110 organic ligand Substances 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 125000001997 phenyl group Chemical group [H]C1=C([H])C([H])=C(*)C([H])=C1[H] 0.000 description 1
- 229910052698 phosphorus Inorganic materials 0.000 description 1
- 239000011574 phosphorus Substances 0.000 description 1
- 238000001782 photodegradation Methods 0.000 description 1
- 239000003504 photosensitizing agent Substances 0.000 description 1
- 231100000572 poisoning Toxicity 0.000 description 1
- 230000000607 poisoning effect Effects 0.000 description 1
- 229920006389 polyphenyl polymer Polymers 0.000 description 1
- 229920002223 polystyrene Polymers 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000004445 quantitative analysis Methods 0.000 description 1
- 238000006862 quantum yield reaction Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 238000006479 redox reaction Methods 0.000 description 1
- 238000004153 renaturation Methods 0.000 description 1
- 230000002441 reversible effect Effects 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 230000008054 signal transmission Effects 0.000 description 1
- 238000003980 solgel method Methods 0.000 description 1
- 238000011895 specific detection Methods 0.000 description 1
- 238000004611 spectroscopical analysis Methods 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 238000010183 spectrum analysis Methods 0.000 description 1
- 230000006641 stabilisation Effects 0.000 description 1
- 238000011105 stabilization Methods 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000001308 synthesis method Methods 0.000 description 1
- 230000002194 synthesizing effect Effects 0.000 description 1
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Abstract
A kind of preparation method of the titanium dioxide nano-particle fluorescence probe for DDT detection, including with TiO2For core, the chloro- 7- nitrobenzofuran fluorescence probe of 4- and aminopropyl functional group in its surface modification form silica trace shell finally in its surface imprinted class target molecule.The preparation process of above-mentioned fluorescence probe is divided into three steps: (1) preparation of fluorescence presoma;(2) silanization of class target molecule;(3) preparation and elution of the titanium dioxide nano-particle of trace class target molecule.Target molecule DDT enters recognition site, the chlorine atom of DDT and the hydrogen atom of aminopropyl form hydrogen bond, stablize aminopropyl, when light excites, prevents the electronics transfer of nitrogen-atoms on aminopropyl to NBD-APTS compound, according to Photo-induced electron transfer mechanism, the enhancing for leading to complex fluorescence intensity realizes the identification and detection to DDT molecule by the matching of imprinted sites and the change of fluorescence intensity, by changing excitation wavelength, TiO is excited2The degradation to DDT molecule is realized in photocatalysis.
Description
Technical field
The present invention relates to materials science fields, in particular to the titanium dioxide nano-particle fluorescence probe of DDT detection
Preparation method.
Background technique
In secure context, also to the Ecological environment and human body in China while the use of pesticide brings enormous benefits for us
Health causes serious threat.Especially residual of the pesticide in pesticide herd product and food has chronic toxicity, straight to human body
Connect poisoning, " three cause " (carcinogenic, teratogenesis, mutagenesis) effect and environmental hormone effects.Pesticide residue constitutes China's food safety
Long-term, serious threat, the public is decreased obviously the sense of security of agricultural product and food, while also having seriously affected China's agriculture
Competitiveness of the product in international market.Therefore, in recent years, to the detection of trace pesticide and the exploration of relevant sensor array
Society research mechanism has been caused widely to pay close attention to and fruitful exploration.There are many method of detection DDT at present, chromatography
In, high performance liquid chromatography, liquid matter and gas chromatography mass spectrometry are more common methods.These conventional analytical techniques can satisfy in analysis
Basic demand, such as selectivity, reliability, accuracy and repeatability, still, these detection methods need accurate equipment and
Professional operator is expensive, time-consuming and cumbersome bulky in these processes, and in detection, sample must be
It is detached from detection scene and is sent to laboratory for analysis, can not accomplish the detection of real-time on-site.More popular detection is applied now
Technology is hexavalent chrome bio-removal and enzyme assay.Biosensor (Biosensor) is that one kind is identified with biomaterial to be sensitive
Element, a kind of device being made of signal conversion element and signal transmitting element have highly sensitive, stronger specificity, operation
The convenient, advantages such as instrument and equipment expense is low, but existing biosensor there are still testing results unstable, poor reproducibility and make
With the service life it is short the problems such as.Enzyme assay is mainly based upon organic phosphorus and carbamate to acetylcholine esterase active
Inhibiting effect and a kind of analytic approach developed, detection process are simple, but the accuracy of this analysis method is poor, and detection limit is big
Mostly at ppm grades, false positive, false negative are caused, qualitative analysis is generally used for.In summary, it is necessary to seek to DDT mesh in environment
Mark analyte provides a kind of highly selective, highly sensitive, quick response, the method for low cost and in situ detection.
In application aspect, detection technique how is improved to the selectivity of DDT target analytes.Molecular imprinting technology is as one
The mature technology of kind is widely used in the molecularly imprinted polymer (molecularly that synthesis has specific recognition site
Imprinted polymers, MIPs).Prepared molecularly imprinted polymer have wide applicability, good plasticity,
Stability and it is highly selective the advantages that, internal recognition site can be selectively in conjunction with template molecule, to realize
Selective recognition.The preparation process of MIPs is generally divided into three steps: (1) (target analytes are similar with template molecule for function monomer
Object) by covalently or non-covalently effect form monomer-template composite;(2) under conditions of initiator or photoinduction, this is multiple
Object and the crosslinking agent effect of being copolymerized are closed, highly cross-linked rigid macromolecule polymer is obtained;(3) by template molecule from polymer
It is removed in skeleton, leaves in three-dimensional cross-linked polymer and all match with template molecule in terms of shape, size
Specific trace binding site, target analytes can be selectively coupled in polymer by binding site.From system
Standby process is it is found that pass through the available structural material being previously set of engram technology;And by being crosslinked, polymer is improved
Stability and the ability for resisting environmental disturbances;The recognition site of polymer surfaces has efficient selectivity to target analytes.Cause
It is specific for these of imprinted polymer, in chemistry and biosensor (Liang R N.Angew. Chem. Int. Ed.,
2010,49(14): 2556-2559;Alizadeh T.Biosens. Bioelectron., 2010,25(5): 1166-1172;
Lakshmi D. Anal. Chem., 2009,81(9): 3576-3584.), Solid Phase Extraction (Sancho R.Chem. Soc. Rev., 2009,38(3): 797-805;Li Y.Nanoscale, 2011,3(1): 280-287;Xu S F.J. Mater. Chem., 2011,21(32): 12047-12053.), it is catalyzed (Orozco J.J. Am.Chem. Soc., 2013,135(14):
5336-5339;Li S J.Adv. Funct. Mater., 2011,21(6): 1194-1200;Wulff G.Acc. Chem. Res., 2012,45) and UF membrane (Wang J Y. (2): 239-247.J. Membr. Sci., 2009,331(1-2): 84-
90;Tasselli F.J. Membr. Sci., 2008,320(1-2): 167-172;Jiang Y. J. Membr. Sci.,
2006,280(1-2): 876-882.) etc. fields have wide practical use.In recent years, patent of invention (CN105403694):
It is " a kind of for detecting the PS@SiO of paraquat molecule2The preparation method of artificial antibody " is reported with coated with silica polyphenyl second
Alkene (Polystyrene, PS) microballoon forms core-shell structure.The final step of imprinted polymer is prepared, SiO is eluted2In shell
Template molecule, SiO2The inside of shell, which is formed, has the function of the hole complementary with template molecule structure, size and base, obtains
Trace microballoon have the specific recognition site of target analyte molecule is realized to the Selective recognition of paraquat molecule and
Detection.2012, East China Normal University master Zhang Dan, thesis " nano-material surface molecular imprinting technology research and its
To the specific recognition of pesticide " in, using molecular engram-electrochemistry joint technology, received with function alloy nano particle, multi wall carbon
As reaction carriers, synthesizing, there is a variety of nano materials with satisfactory electrical conductivity such as mitron the novel molecular of good selectivity to print
Mark material is successfully realized the highly sensitive specific detection to pesticide several frequently seen in actual sample.
The selectivity to target analytes can be improved in engram technology, but lacks signal transmission in analysis detection application
Ability cannot reach the requirement of quick response.And fluorescent molecule is the highly sensitive response ideal material to target analytes.Each
In kind signal transducer, the optically addressable sensor based on fluorescence "Off" or fluorescence "ON" mechanism has proven to researcher
The method to various small molecule target analysis analyte detections is expected in the environment of many challenges.Fluorescent optical sensor is generally by three
Divide and constitute: fluorophor, recognition group and linking group.Fluorophor refers to the portion that Self-variation can be changed into fluorescence signal
Point;Recognition group refers to can be in conjunction with target analytes and the part that changes a lot;Linking group then refers to and connects the two
Pick up the part come.Based on different principles, there are Photo-induced electron transfer (PET) fluorescent optical sensor, fluorescence resonance energy transfer
Fluorescent optical sensor, rare earth chelating luminous fluorescent sensor and Intramolecular electron transfer fluorescent optical sensor.It is analyzed based on different target
Object and reaction condition select different fluorescence reaction devices.Based on fluorescence resonance energy transfer principle, patent of invention is disclosed
(CN104359880) " to the chemical preparation process of the CdTe quantum fluorescence probe of trace paraquat detection ", obtained CdTe
Quantum dot fluorescence probe, the negatively charged carboxyl in surface and positively charged target analysis molecule paraquat pass through positive and negative charge
Electrostatic interaction, when spatially close to each other with paraquat, by fluorescence resonance energy transfer principle, emission spectrum is red
CdTe quantum fluorescence probe photoluminescent band can by green paraquat molecule absorption, utilize CdTe quantum fluorescence intensity
Change, realize the detection to trace paraquat.Principle is chelated based on rare earth, discloses patent of invention (CN106092983)
A kind of " detection organo-chlorine pesticide Y2O3: Tb3+@SiO2-NH2The preparation method of fluorescent sensor array ", Y2O3: Tb3+@SiO2-NH2
Print identification site inside fluorescent sensor array can interact with organo-chlorine pesticide molecule (target molecule), make organochlorine
Tb on pesticide molecule and recognition site3+Coordination forms organic ligand, utilizes metal ion Tb3+The change of fluorescence intensity is realized
Detection to organo-chlorine pesticide molecule.2016, University of Anhui master Yu Shenglong was " female based on cumarin and quinoline in thesis
In the research of the small molecule fluorescent chemical sensor of body ", first reports one based on Intramolecular electron transfer (ICT) mechanism
Two-photon fluorescence probe (TNQ), for detecting hydrazine hydrate, and the detection of hydrazine hydrate steam in environment can be advantageously applied to
In bio-imaging.In the present invention, it is based on photoinduction molecule principle of transfer, the titanium dioxide for having synthesized a kind of couple of DDT detection is received
Rice corpuscles fluorescence probe.The amino on print identification site inside titanium dioxide nano-particle fluorescence probe can be identified with entering
The DDT interaction of molecules in site, the chlorine atom on amino on hydrogen atom and DDT molecule forms hydrogen bond, so that amino is stablized, resistance
Fluorophor transfer of the electronics on amino on recognition site is hindered, it is suppressed that the fluorescence of fluorophor is quenched on recognition site
It goes out, leads to the fluorescence enhancement of fluorophor on recognition site, realize the detection to DDT.Moreover, in recent years, Photoinduced Electron turns
(PET) reaction is moved to have made great progress in terms of induced fluorescence molecular recognition.Due to the detection method high RST output and
Reliable testing result, the chemical sensor of fluorescence "ON" mechanism are extremely beneficial to the detection of DDT class pesticide.Detect DDT
Whether entering molecularly imprinted polymer recognition site is exactly the mechanism according to Photo-induced electron transfer.DDT molecule enters titanium dioxide
The print identification site of titanium nanoparticle fluorescence probe interior can interact with the aminopropyl on recognition site, on aminopropyl
Chlorine atom on hydrogen atom and DDT molecule forms hydrogen bond, stablizes aminopropyl, when light excites, prevents nitrogen-atoms on aminopropyl
Electronics transfer leads to the enhancing of complex fluorescence intensity, fluorescence according to Photo-induced electron transfer mechanism to NBD-APTS compound
The increased degree of intensity depends on the size of Hyarogen-bonding.2005, Dalian Inst of Chemicophysics, Chinese Academy of Sciences announced
Method, that is, fluorescence of patent of invention (CN1632538A) " a kind of method that pesticide residue high sensitivity quickly detects ", report passes
Sensor.Using fluorescence probe as indicator, the inhibition of organophosphorus pesticide and carbamate chemicals for agriculture to cholinesterase activity is indicated
Degree, or the told pesticide of instruction measure pesticide by the variation of fluorescence intensity to the process of organophosphor hydrolytic enzyme hydrolysis
Residual quantity.This method limits the detection of organophosphorus pesticide and carbamate chemicals for agriculture, using Furadan as standard substance, Ke Yida
To 2 μ g/kg.
In conclusion the efficient selective of engram technology and the quick response of fluorescent optical sensor, obtain more and more researchs
The favor of person.And combine the two, i.e., it is constructed using molecularly imprinted polymer as the recognition component of sensor material, for detecting
Pesticide residue, while very high selection specificity to target analytes and being exaggerated detection output signal.In recent years, also there is portion
The branch person of grinding is after studying molecular imprinting technology and fluorescent optical sensor combination, for detecting pesticide residue.
2013, Institute of Quality Standards and Testing Technology for Agri-Products, Chinese disclosed patent of invention
(CN103558203) " magnetic molecularly imprinted polymer-fluorescence analysis method ", it was recently reported that with magnetic molecularly imprinted biomimetic material,
Instead of being commonly used in general rapid detection method but being difficult to the natural antibody prepared, by pesticide molecule and fluorescence probe to magnetism
The competition of imprinted polymer, the nonimmune method for technically realizing triazine quickly detect.And the magnetic print of invention
Mark polymer is conducive to the enrichment and separation of pesticide molecule.2015, University Of Tianjin disclosed patent of invention
(CN105092548) " a method of p-nitrophenol is detected based on molecular engram Ratiometric fluorescent probe ", the fluorescence
Nanoparticle is to grow one layer of silicon dioxide layer containing microsphere nitrophenol on its surface, obtains the double fluorescence of molecular engram
Composite nanoparticle.In this configuration, the quantum dot positioned at the Nano particles of silicon dioxide inside is as reference fluorescent signal, outside
Carbon dots fluorescence signal in response in layer molecular engram layer, the Selective recognition for p-nitrophenol.The method overcome
The single fluorescence signal analysis method of tradition disadvantage easily affected by environment.2016, Jiangsu University doctor Wei Xiao was in thesis
In " preparation of CdTe quantum molecular engram composite fluorescence sensor and its Selective recognition and fluorescent detection capabilities research ", with
The CdTe quantum of thiomalic acid (MSA) modification is fluorescence carrier, APTES(3- aminopropyl triethoxysilane) it is function list
Body, TEOS(ethyl orthosilicate) it is crosslinking agent, cyfloxylate (LC) is template molecule, with the reverse microemulsion method amount of being successfully prepared
Son point molecular engram fluorescent optical sensor (CdTe@SiO2@MIPs).Utilize TEM, SEM, FT-IR and molecular fluorescence spectrophotometer
Equal characterization methods have studied CdTe@SiO2Shape characteristic, structure composition and the optical property of@MIPs.Fluorescence detection experiments have shown that
LC can make CdTe@SiO2@MIP fluorescence quenches, and is linearly closing in the concentration range memory of 5.0 ~ 60 μm of ol/L
System.Selective recognition description of test CdTe@SiO2@MIP has apparent Selective recognition ability to LC.The analysis finally established
Method is successfully applied to the detection of LC concentration in practical water body.
But still in the primary stage, there is also many problems to need to solve for the research of molecular engram fluorescent optical sensor, needs
More molecular engram production of fluorescent sensor and detection architecture are developed, and this can become always the master of modern development
Topic.
Fluorescent optical sensor is generally divided into three classes: organic dyestuff fluorescent optical sensor, rare-earth fluorescent sensor and quantum dot fluorescence
Sensor.Organic fluorescent dye stable structure, fluorescence quantum yield is higher, but organic fluorescence marker excitation spectrum and transmitting light
Stokes displacement between spectrum is smaller, carries out interference vulnerable to exciting light when fluorescence detection, while also vulnerable to coming from background
Fluorescence, stray light (Tyndall, Rayleigh, Raman) etc. seriously affect.In addition, polarity, pH value, for a long time excitation photograph
Penetrate, oxygenated water it is gentle with other heavy atoms or absorb group close to etc. the variations of external environments can all cause the change of fluorescence intensity
Change, leads to fluorescent quenching or the generation of photobleaching phenomenon (Ye Zhangmei, Shanghai University's master thesis, 2011).In order to reduce
Influence of the background to organic dyestuff, selecting some performances, good material wraps up it, such as silica and titanium dioxide
Deng, and then form core-shell structure.Luminescent dye molecule is surrounded by three-dimensional silica network system, can overcome the external world
Influence of the environment to fluorescent material has completely cut off the influence of extraneous oxygen or other fluorescent quenching substances to fluorescent dye in shell, shows
Work improves its photostability, hence it is evident that extends fluorescence lifetime.And thousands of can be embedded in a fluorescent nano particle
Fluorescent molecule, fluorescent label signal significantly increase, and detection sensitivity significantly improves.
One patent of invention (US20100261244) " Method for immobilizing bio- in the U.S.
material on titanium dioxide nanoparticles and titanium dioxide nanoparticles
Immobilized by bio-material ", it was recently reported that a kind of that biological high reflection material is fixed on titania nanoparticles
The method on surface, it is therefore an objective to improve the sensitivity of resonant reflectance biosensor.Titanium dioxide nano-particle is because of optical stabilization, nothing
The advantages that malicious and cheap, is widely used in preparing fluorescence probe (CN1707244A;CN105806923;CN102010712), tie
Fruit shows that titanium dioxide is easy balling-up, and fluorescence presoma is easily adhered on surface, thus the core-shell structure fluorescent nanometer microsphere of preparation
Function admirable.
In the present invention, we, which report, is received based on Photo-induced electron transfer principle in the rich amino-containing titanium dioxide in surface
Rice corpuscles realizes the detection to DDT.According to elaboration before, it can be seen that titanium dioxide nano-particle is very suitable to be prepared into
Fluorescence probe, because the titanium dioxide nano-particle fluorescence probe optical clear in visible-range, and have photon physics lazy
Property and its surface can be easy to by with subunit that upper new assembling function is modified and silylating reagent condensation reaction.Dioxy
Hydrogen bond can be formed with DDT target molecule by changing the nanoparticle surface modified amino of titanium, since there are electron delocalization, this charges
Transfer complex shows a very strong visible absorbance peak in 532nm wavelength.The discovery of this result, excites us in dioxy
Change titanium nanoparticle surface and passes through covalent cross-linking 3- aminopropyl triethoxysilane (3-
Aminopropyltriethoxysilane, APTS) explore the chemical sensor based on Photo-induced electron transfer mechanism to DDT
Highly selective, the highly sensitive detection of target molecule.Select a suitable fluorescent material, fluorescence emission spectrum and APTS-DDT
The absorption spectrum of the ultraviolet-visible of compound coincides, and when they are spatially close to each other, the fluorescence of fluorescent material passes through
The hydrogen bond enhancing formed between APTS-DDT, it is suppressed that fluorescence is quenched.Due to titanium dioxide nano-particle surface there are many
To the very strong amino subunit of DDT combination sensibility, thus the fluorescence probe that is prepared into can selectivity to DDT target in environment
Molecule forms quick response.It is former to pass through Photo-induced electron transfer for this surface modification titanium dioxide nano-particle of APTS
Reason, is able to detect that the DDT of nanomolar concentration grade in the liquid phase.This fluorescence dioxy to DDT molecule with the specially property known effect
Change titanium nanoparticle to show highly selective to DDT, highly sensitive and trace using fluorescence as probe, amino as recognition site
Detection.
In addition, titanium dioxide have excellent photocatalysis performance, using titanium dioxide this characteristic can further by
Pesticide D-D T degradation, becomes nontoxic carbon dioxide, hydrone and other ions.The energy band of titanium dioxide semiconductor is discontinuous
, it is to be made of valence band and conduction band, has a band gap i.e. forbidden band between this two parts, the width of forbidden band is 3.2eV, so working as
Light is radiated at TiO2When grain surface, can absorbing wavelength≤387.5nm near ultraviolet light wave, the electronics in valence band will be by this time
It is energized into conduction band, while generating corresponding hole in valence band, forms photo-generate electron-hole pairs.Electrons and holes are in internal electricity
It separates under the action of, and is migrated in catalyst surface to different directions, and then redox reaction occurs on surface.
For Gong Lifen etc. studies have shown that after daylight light irradiation 30min, the nTiO of cerium is adulterated in photosensitizer modification2To six six six, DDT
(DDD), the photodegradation rate of the organo-chlorine pesticides such as DDT her (DDE) reaches 85% or more.When illumination 45min, solution rate up to 95% with
Upper (Xiamen University's journal, 2008,7(1): 79-82).Li Meijin etc. is with TiCl4For raw material, rutile titania is prepared for using Hydrolyze method
Mine type nano-TiO2.Have studied the agricultures containing chlorine such as α, β, γ, δ-six six six (BHC), DDT, dieldrite, dicofol, heptachlor
Medicine is in nano-TiO2Suspension system and action of ultraviolet light under degradation behavior.Due to the relationship of C-Cl bond energy, different organochlorines
The disposal efficiency of pesticide is very different, and wherein the degradation rate of dicofol is up to 70%, and the degradation rate of dieldrite is
45%, DDT is 23%, the degradation rate of heptachlor minimum 14%.In 4 kinds of BHC isomers, the conversion ratio highest of α-BHC, light
According to substantially completely, the conversion ratio of β-BHC is relatively low for degradation after 4h, have 40% or so, degradation rate sequence is α-BHC > γ-
BHC > δ-BHC > β-BHC(Spectroscopy and spectrum analysis, 2008,8(6): 1364-1367).It can from the research of forefathers
Out, the efficiency of titanium deoxide catalyst degradation DDT is relatively low, so, improve the research of Titanium Dioxide degradation DDT efficiency also
Continuing.
In the present invention, under visible light, the titanium dioxide nano-particle fluorescence probe with target molecule DDT of preparation pass through
Photo-induced electron transfer principle carries out recognition detection, and the fluorescence probe of DDT is loaded with after detection, glimmering in the case where being less than 387.5nm wavelength
DDT in light probe is degraded because of the photocatalysis of titanium dioxide.Currently, yet there are no in the modification of titanium dioxide shell layer surface
Amino, and then the glimmering of titanium dioxide nano-particle preparation is utilized to the report of DDT trace detection, and without pertinent literature report
Light probe first detects the research degraded afterwards to DDT.So the titanium dioxide nano-particle fluorescence that synthesis is highly selective and highly sensitive
The preparation method of probe is realized to identification, detection and the degradation in situ of DDT molecule, there is its necessity.
Summary of the invention
Goal of the invention: for shortcoming existing for currently available technology, using titanium dioxide as core, in its surface modification
The chloro- 7- nitrobenzofuran fluorescence probe of 4- and aminopropyl functional group form two finally in its surface imprinted class target molecule
Silica trace shell obtains core-layer-shell mould fluorescence probe particle, has invented the dioxy with amino of a kind of couple of DDT detection
Change the preparation method of titanium nanoparticle, and titanium dioxide nano-particle surface progress functional modification is used for trace for the first time
Identification, detection and the degradation of DDT molecule.The method is chemical synthesis, has nanoscale with sol-gel method synthesis
The DDT molecular blotting polymer microsphere of size.The chloro- 7- nitrobenzofuran (4-chloro-7- of fluorescer 4- first
Nitrobenzofurazan, NBD-Cl) and function monomer APTS reaction, obtain NBD-APTS compound, i.e. fluorescence presoma;
Then, 4,4 '-ethylenebis phenol (4,4 '-Ethylidenebisphenol, EDA) (DDT analog) are used as template molecule,
It is reacted with 3- isocyano group propyl-triethoxysilicane (ICPTS), obtains EDA-ICPTS compound.In dehydrated alcohol, ammonium hydroxide is made
For catalyst, ethyl orthosilicate (Tetraethoxysilane, TEOS) is used as crosslinking agent, and butyl titanate hydrolyzes to obtain titanium dioxide
Microballoon is reacted with above two compound respectively, finally obtains DDT molecular blotting polymer microsphere.
The technical scheme is that a kind of preparation side of the titanium dioxide nano-particle fluorescence probe for DDT detection
Method, it is characterised in that: the amino on print identification site inside the titanium dioxide nano-particle fluorescence probe can be with entrance
The DDT interaction of molecules of recognition site, the chlorine atom on hydrogen atom and DDT molecule on aminopropyl form hydrogen bond, make ammonia third
Base is stablized, and when light excites, prevents the electronics transfer of nitrogen-atoms on aminopropyl to NBD-APTS compound, is turned according to Photoinduced Electron
Telephone-moving reason, leads to the enhancing of complex fluorescence intensity, by the matching of imprinted sites and the change of fluorescence intensity, realizes to DDT
The identification and detection of molecule, preparation process include following three step:
The preparation of 1.1 NBD-APTS compounds: firstly, with electronic balance precise 0.0010g ~ 0.0030g 4-
Chloro- 7- nitrobenzofuran (4-chloro-7-nitrobenzofurazan, NBD-Cl) is placed in the mono- neck ground flask of 50mL,
Then, then with the microsyringe that range is 100 μ of μ L ~ 1000 L draw the 220 μ L 3- aminopropyl-triethoxy silicon of μ L ~ 230
Alkane (3-aminopropyltriethoxysilane, APTS) is added in above-mentioned flask, finally, 10mL is added into flask again
~ 20mL ethyl alcohol stirs mixture ultrasonic disperse 4min ~ 6min in flask in an inert atmosphere with 400rpm ~ 600rpm
It mixes speed and reacts 1h ~ 3h at 50 DEG C;
The preparation of 1.2 EDA-ICPTS compounds: using electronic balance precise 0.4230g ~ 0.4250g 4 first,
4 '-ethylenebis phenol (4,4 '-Ethylidenebisphenol, EDA) are placed in the mono- neck ground flask of 100mL, then, then
1000 μ L 3- isocyanide propyl-triethoxysilicane (3- are drawn with the microsyringe that range is 100 μ of μ L ~ 1000 L
Isocyanatopropyltriethoxysilane, ICPTS) it is added in above-mentioned flask, it is eventually adding 10mL ~ 20mL second
Alcohol, by mixed liquor ultrasonic disperse 7min ~ 9min in above-mentioned 100mL flask, in an inert atmosphere, with 400rpm ~ 600rpm
Mixing speed reacts 5h ~ 7h at 50 DEG C;
Prepared by the titanium dioxide nano-particle of the trace class target molecule of 1.3 surface modification amino and fluorophor: respectively
The butyl titanate of the ethanol solution and 2mL ~ 4mL that measure 60mL ~ 80mL is placed in ultrasonic mixing in 250mL flask, then again
The above-mentioned NBD-APTS complex solution prepared is added, 2min ~ 4min is stirred with 450rpm ~ 550rpm at room temperature,
The EDA-ICPTS complex solution prepared then is added, finally, the 500 μ L ammonium hydroxide of μ L ~ 1000 and 440 μ of μ L ~ 460
L ethyl orthosilicate (Tetraethoxysilane, TEOS) is added in above-mentioned reaction solution, with 700rpm ~ 800rpm stirring
After 3min, speed of agitator is down to 450rpm ~ 550rpm, reacts at room temperature for 24 hours, obtains surface modification amino and fluorophor
Trace class target molecule titanium dioxide nano-particle, the 50mL mixed solution for being then 4:1 with ethyl alcohol and acetone volume ratio
Elute class target molecule;
At 90 DEG C, by the titanium dioxide nano-particle of above-mentioned elution class target molecule 60mL concentration be 0.25mol/
Flow back 2h in the tetrahydrofuran solution of the Lithium Aluminium Hydride of L, then cleans removal three times with anhydrous tetrahydro furan and be adsorbed on titanium dioxide
Extra Lithium Aluminium Hydride in nanoparticle surface, obtain containing amino, fluorophor to target molecule have selection identification, detection
Titanium dioxide nano-particle fluorescence probe.
As a further improvement of existing technologies, described fluorescence probe is titanium dioxide nano-particle, surface cladding
A thin layer silica, partial size can be controlled by adjusting the dosage of butyl titanate;Described titanium dioxide nano granule
Sublist face makes its surface rich in amino through modification;Described silylating reagent is 3- isocyano group propyl-triethoxysilicane;Described quilt
Identification molecule is DDT;The amino on described titanium dioxide nano-particle surface is capable of the combination DDT target molecule of the special property known, and is formed
Hydrogen bonding compound;Described titanium dioxide nano-particle surface residue amino can form hydrogen bond with DDT, inhibit electronics transfer, make
Fluorescence enhancement;Described titanium dioxide nano-particle, in the case where being less than 387.5nm wavelength, can degrade DDT.
Compared with the existing technology the utility model has the advantages that
In recent years, the domestic method for detecting DDT, common or chromatography.Using gas chromatography (GC) to gold
BHC(α-BHC, β-BHC, γ-BHC, δ-BHC in line lotus), DDT (PP '-DDE, PP '-DDD, OP '-DDT, PP '-DDT) 8
The kind remaining limit detection of organic chlorine agriculture chemicals.It obtains a result: linear good, the phase relation of BHC, DDT standard working curve
Number 0.9988~0.9997, average yield 95.4%~98.9%, SD are 1.00%~2.98%.Detection is limited to 0.0053~0.021 μ
g/L.Measurement result is shown: β-BHC be 0.000 9 mg/kg(wherein α-BHC, γ-BHC, δ-BHC, PP'-DDE, OP'-DDT,
PP'-DDD, PP'-DDT are not detected).This method of drawing a conclusion sensitivity and linear measurement range with higher, measurement result are accurate
Reliably, science it is feasible, for BHC in roxburgh anoectochilus terminal bud and DDT pesticide residue quality monitoring (Chinese Traditional and Herbal Drugs, 2016,47, 4082-4084.).It is extracted using acetonitrile, the purification of Full-automatic solid phase extraction instrument turns evaporation
Instrument concentration;It is analyzed by mass spectrometry after the separation of DB-1701 capillary column, with selective ion detection mode, with daughter ion abundance
Than qualitative, mark standard measure.Six six six and the good (related coefficient of DDT linear relationship within the scope of 4~160ppb mass concentration
It is all larger than 0.99), method detection is limited to 0.10~2.15ppb.The recycling of two pitch-based spheres of six six six and DDT in rice husk
Rate is 84.2%~109.7%, and the relative standard deviation (RSD) of renaturation is between 4.3%~7.4%.This method is accurate and reliable, is used for
In rice husk six six six and DDT pesticide residue qualitative and quantitative analysis (Liquor-Making Science & Technology, 2016,9, 79-82.).
But discussed before, although chromatography can satisfy accurate and qualitative, quantitative requirement, but need accurate set
Standby and professional operation, it is time-consuming, laborious, and it is unable to real-time on-site detection.Other detection sides are developed for these reasons
Method, and microsphere fluorescence probe is research hotspot, yet there are no and modifies amino and NBD-Cl in titanium dioxide surface, in conjunction with print
The document of the detection of mark technology and degradation DDT.Therefore, the preparation side of highly selective and highly sensitive microsphere fluorescence probe is synthesized
Method realizes identification in situ, detection and degradation to DDT molecule, there is its necessity.
The present invention is the preparation of NBD-APTS compound and EDA-ICPTS compound first: using electronic balance precise
0.0010g ~ 0.0030g NBD-Cl is placed in the mono- neck ground flask of 50mL, is 100 μ of μ L ~ 1000 L's with range then
1000 μ L microsyringes are drawn the 220 μ L of μ L ~ 230 APTS and are added in above-mentioned flask, finally, being added again into flask
10mL ~ 20mL ethyl alcohol, by 4 ~ 6min of mixture ultrasonic disperse in flask, in an inert atmosphere, with 400rpm ~ 600rpm
Mixing speed reacts 1h ~ 3h at 50 DEG C.It is placed in simultaneously with electronic balance precise 0.4230g ~ 0.4250g EDA
In the mono- neck ground flask of 100mL, then, then with range be 100 μ of μ L ~ 1000 L microsyringe draw 1000 μ L ICPTS
It is added in above-mentioned flask, is eventually adding 10mL ~ 20mL ethyl alcohol, by mixed liquor ultrasonic disperse 7min in above-mentioned 100mL flask
~ 9min reacts 5h ~ 7h in an inert atmosphere with 400rpm ~ 600rpm mixing speed at 50 DEG C.
Secondly, the preparation of the titanium dioxide nano-particle of the trace class target molecule of surface modification amino and fluorophor:
The butyl titanate of the ethanol solution and 2mL ~ 4mL that measure 60mL ~ 80mL respectively is placed in 250mL flask, is added above-mentioned
The NBD-APTS complex solution prepared stirs 2min ~ 4min at room temperature with 450rpm ~ 550rpm, then adds again
Enter the EDA-ICPTS complex solution prepared, then the 500 μ L ammonium hydroxide of μ L ~ 1000 and the 440 μ L TEOS of μ L ~ 460 are added
Into above-mentioned reaction solution, it is seen that under light, with 700rpm ~ 800rpm stir 3min after, speed of agitator be down to 450rpm ~
550rpm reacts at room temperature and obtains the titanium dioxide of the trace class target molecule of surface modification amino and fluorophor for 24 hours and receive
Then rice corpuscles elutes class target molecule with the 50 mL mixed solutions that ethyl alcohol and acetone volume ratio are 4:1.
At 90 DEG C, by the titanium dioxide nano-particle of above-mentioned elution class target molecule 60mL concentration be 0.25mol/
Flow back 2h in the tetrahydrofuran solution of the Lithium Aluminium Hydride of L, then cleans removal three times with anhydrous tetrahydro furan and be adsorbed on titanium dioxide
Extra Lithium Aluminium Hydride in nanoparticle surface, obtain containing amino, fluorophor to target molecule have selection identification, detection
Titanium dioxide nano-particle fluorescence probe.
In conclusion the titanium dioxide nano-particle of surface modification amino, is especially wrapped on titanium dioxide nano-particle
Covered layer of silicon dioxide, not only increased the specific surface area of fluorescence probe, but also increased molecular recognition site, improve selectivity,
Identity and sensibility.
Second, the surface modification titanium dioxide nano-particle fluorescence probe of amino, can know DDT molecular selection
Not.Detect whether DDT enters molecularly imprinted polymer recognition site, the hydrogen on aminopropyl according to Photo-induced electron transfer mechanism
Chlorine atom on atom and DDT molecule forms hydrogen bond, stablizes aminopropyl, when light excites, prevents the electricity of nitrogen-atoms on aminopropyl
Son is transferred to NBD-APTS compound, according to Photo-induced electron transfer mechanism, leads to the enhancing of complex fluorescence intensity.
Third, the titanium dioxide nano-particle fluorescence of surface modification amino is visited compared with traditional rare-earth luminescent material
Needle set has biggish specific surface area, possesses recognition site, improves to target molecule Selective recognition, is turned using Photoinduced Electron
Principle is moved, the sensitive detection of the height to target analytes is improved.
Fourth, titanium dioxide nano-particle partial size and thickness are controllable in method provided by the present invention, adjusting can be passed through
The dosage of butyl titanate is controlled.
Fifth,, there is the following in the reason of selection titanium dioxide: (1) being readily synthesized TiO 2 sol, have biggish
Specific surface area needs relatively low cost;(3) during the reaction, there is stability chemically and thermally, not with organic solvent
Reaction;(4) surface is easy grafting organo-functional group;(5) environmental sound;(6) there is excellent photocatalysis performance, work as light energy
When greater than forbidden bandwidth, electronics hole pair is generated, has the ability of degradation DDT, DDT is degraded to nontoxic organic molecule.
Sixth, the analog EDA of DDT first is combined by way of covalent bond with ICPTS, then with NBD-APTS with non-
The form of covalent bond (hydrogen bond) combines, it is suppressed that fluorescent quenching, therefore fluorescence enhancement.This mixed molecules engram technology compensates for
The shortcomings that covalent bond and non-covalent bond molecular imprinting technology.
Detailed description of the invention
Fig. 1 is the rich amino-containing titanium dioxide nano-particle fluorescence probe schematic diagram in surface of the present invention.
Fig. 2 is the rich amino-containing titanium dioxide nano-particle fluorescence probe in surface of the present invention and DDT target point
Detection schematic diagram highly selective to DDT, highly sensitive is realized by Photo-induced electron transfer principle between son.
Fig. 3 is titanium dioxide nano-particle fluorescence probe scanning electron microscope diagram of the present invention.
Fig. 4 is titanium dioxide nano-particle fluorescence emission spectrogram of compound of the present invention and under 365nm ultraviolet lamp
Optical photograph.
Fig. 5 is the trace class target molecule of the surface modification amino and fluorophor before and after reflux of the present invention
The infrared spectrum of titanium dioxide nano-particle.
Fig. 6 is that the fluorescence after titanium dioxide nano-particle fluorescence probe contact measured substance DDT of the present invention increases
Qiang Tu.
Fig. 7 is adsorption isothermal curve figure of the DDT of the present invention on trace microballoon and non-trace microballoon.
Fig. 8 is the dynamic absorption curve graph of DDT molecular engram microsphere of the present invention Yu non-trace microballoon.
Specific embodiment is explained further with reference to the accompanying drawings
Fig. 1 is the rich amino-containing titanium dioxide nano-particle fluorescence probe schematic diagram in surface of the present invention.In Fig. 1
In, it is the preparation of NBD-APTS compound and EDA- ICPTS compound respectively first: uses electronic balance precise NBD-Cl,
It is placed in single neck ground flask, then draws APTS again, be added in above-mentioned flask, finally, ethyl alcohol is added into flask again, it will
Mixture ultrasonic disperse 5min in flask reacts 2h at 50 DEG C with 500rpm mixing speed in an inert atmosphere.Electricity consumption simultaneously
Sub- balance precise EDA is placed in single neck ground flask, then draws ICPTS again, is added in above-mentioned flask, finally plus
Enter ethyl alcohol, it is in an inert atmosphere, anti-at 50 DEG C with 500rpm mixing speed by mixed liquor ultrasonic disperse 8min in above-mentioned flask
Answer 6h.It is the preparation of the titanium dioxide nano-particle of the trace class target molecule of surface modification amino and fluorophor again: respectively
It measures ethanol solution and butyl titanate is placed in 250 mL flasks, add the above-mentioned NBD-APTS complex solution prepared,
3min is stirred with 500rpm at room temperature, then adds the EDA-ICPTS complex solution prepared, then ammonium hydroxide and TEOS
It is added in above-mentioned reaction solution, it is seen that under light, after stirring 3min with 800rpm, speed of agitator is down to 500rpm, at room temperature
Reaction for 24 hours, obtains the titanium dioxide nano-particle of the trace class target molecule of surface modification amino and fluorophor, then uses second
The 50 mL mixed solutions that alcohol and acetone volume ratio are 4:1 elute class target molecule.
The titanium dioxide nano-particle of above-mentioned preparation is flowed back 2h in the tetrahydrofuran solution containing Lithium Aluminium Hydride.Finally
Resulting solution is cleaned into removal three times with anhydrous tetrahydro furan and is adsorbed on tetrahydro extra on surface titanium dioxide nanoparticle
Aluminium lithium, then three times with washes of absolute alcohol, removal are adsorbed on APTS extra on surface titanium dioxide nanoparticle, obtain table
Face there is highly selective, high sensitivity and trace to detect titanium dioxide nano-particle fluorescence probe DDT rich in amino.
Fig. 2 is the rich amino-containing titanium dioxide nano-particle fluorescence probe in surface of the present invention and DDT target point
Detection schematic diagram highly selective to DDT, highly sensitive is realized by Photo-induced electron transfer principle between son.DDT is micro- with polymer
It is combined between hydrogen atom in ball amino with the active force of hydrogen bond.DDT molecule enters in titanium dioxide nano-particle fluorescence probe
The print identification site in portion forms hydrogen bond with the hydrogen atom on aminopropyl, stablizes aminopropyl, when light excites, prevents aminopropyl
The electronics transfer of upper nitrogen-atoms leads to complex fluorescence intensity according to Photo-induced electron transfer mechanism to NBD-APTS compound
Enhancing, pass through the matching of imprinted sites and the change of fluorescence intensity, realize identification to DDT molecule.
Fig. 3 is titanium dioxide nano-particle fluorescence probe scanning electron microscope diagram of the present invention.In this experiment
Using sol-gel synthesis method synthesis of titanium dioxide nanoparticle fluorescence probe, by SEM figure it can be seen that core-layer-shell structure
Titanium dioxide nano-particle be in spherical, uniform particle sizes, surface compact is uniform.
Fig. 4 is the fluorescence emission spectrogram of compound of titanium dioxide nano-particle of the present invention and under 365nm ultraviolet lamp
Optical photograph.Titanium dioxide nano-particle goes out under the transmitted wave excitation of 460nm in the place of 532nm as seen from the figure
Show absorption peak, illustrated that TiO 2 particles fluorescence for green, titanium dioxide nano-particle is placed under the ultraviolet lamp of 365nm,
It can be seen that being really green.
Fig. 5 is the trace class target molecule of the surface modification amino and fluorophor before and after reflux of the present invention
The infrared spectrum of titanium dioxide nano-particle.It is apparent that in figure, in 1620cm-1The flexural vibrations peak at place, amino is being returned
Stream front and back is significantly different, and in the black line before reflux, amino peak is not fairly obvious, almost without, and the red line after flowing back
In amino peak then greatly enhance.Illustrate that reflux so that the amino in titanium dioxide nano-particle increases significantly, has reached elution
The purpose of template molecule.
Fig. 6 is that the fluorescence after titanium dioxide nano-particle fluorescence probe contact measured substance DDT of the present invention increases
Qiang Tu.Using gradually diluted method, it is 1 × 10 that object to be measured molecule DDT, which is configured to concentration,-9 ~ 1×10-5mol∙L-1,
Since being added step-wise in cuvette low concentration, 20 μ L are pipetted with liquid-transfering gun every time, after the cuvette equipped with 2mL is added, are shaken
It shakes uniformly, carries out fluorescence detection.It is apparent that, nanoparticle is at excitation wavelength 460nm, with DDT concentration in figure
Increase, Enhancement of Fluorescence occurs.
Fig. 7 is adsorption isothermal curve figure of the DDT of the present invention on trace microballoon and non-trace microballoon.?
DDT concentration is 1.0 × 10-5 ~ 11.0×10-5mol∙L-1Ethanol solution concentration range in, measure DDT in different traces
With the balance binding capacity in non-imprinted material.Maximum equilibrium adsorption of the DDT on imprinted polymer microballoon is can be found that about in figure
It is 3 times of non-imprinted polymer microballoon maximum equilibrium adsorption capacity, this illustrates that DDT molecular blotting polymer microsphere has preferably DDT
Affinity formd in the polymer and DDT molecular shape this is mainly due to when preparing DDT imprinted polymer microballoon
Match, size is suitable and the hole of functional group that can interact, so that microsphere be made to can be good at into combination
Site generates higher binding capacity.
Fig. 8 is the dynamic absorption curve graph of DDT molecular engram microsphere of the present invention Yu non-trace microballoon.?
10mL concentration is 5.0 × 10-5mol∙L-1DDT ethanol solution in imprinted polymer microballoon 10mg is accurately added, when measuring different
Between imprinted polymer microballoon to the adsorbance of DDT, choose non-nano imprinted polymer measurement different time and the adsorbance of DDT made
For comparative experiments.It can be seen that the nanostructured microsphere and non-nano imprinted structures microballoon of DDT trace changed over time in figure
DDT binding capacity change curve before reaching equilibrium adsorption capacity, adsorb from solution phase by molecularly imprinted polymer nanosphere
The rate of DDT molecule is far longer than the trace titanium dioxide polymer of non-nano structure, and molecularly imprinted polymer nanometer is micro-
It is about 50min that absorption of the ball in solution phase, which reaches the time required for the 50% of maximum equilibrium adsorption capacity, reaches maximum balance
The time of adsorbance is about 120min, and the absorption of conventional print microballoon in the solution reaches the 50% of maximum equilibrium adsorption capacity
Time is about 130min, reaches the time of maximum equilibrium adsorption capacity up to 360min.
Specific embodiment
A kind of preparation method of the titanium dioxide nano-particle fluorescence probe for DDT detection, it is characterised in that: described two
The aminopropyl on print identification site inside titanium oxide nanoparticles fluorescence probe can be with the DDT molecule phase into recognition site
Interaction, the chlorine atom on hydrogen atom and DDT molecule on aminopropyl form hydrogen bond, stablize aminopropyl, when light excites, prevent
The electronics transfer of nitrogen-atoms causes compound glimmering to NBD-APTS compound according to Photo-induced electron transfer mechanism on aminopropyl
The enhancing of luminous intensity realizes identification and detection to DDT molecule by the matching of imprinted sites and the change of fluorescence intensity,
Preparation process includes following three step:
The preparation of 1.1 NBD-APTS compounds: firstly, with electronic balance precise 0.0010g ~ 0.0030g 4-
Chloro- 7- nitrobenzofuran (4-chloro-7-nitrobenzofurazan, NBD-Cl) is placed in the mono- neck ground flask of 50mL,
Then, then with the microsyringe that range is 100 μ of μ L ~ 1000 L draw the 220 μ L 3- aminopropyl-triethoxy silicon of μ L ~ 230
Alkane (3-aminopropyltriethoxysilane, APTS) is added in above-mentioned flask, finally, 10mL is added into flask again
~ 20mL ethyl alcohol stirs mixture ultrasonic disperse 4min ~ 6min in flask in an inert atmosphere with 400rpm ~ 600rpm
It mixes speed and reacts 1h ~ 3h at 50 DEG C;
The preparation of 1.2 EDA-ICPTS compounds: using electronic balance precise 0.4230g ~ 0.4250g 4 first,
4 '-ethylenebis phenol (4,4 '-Ethylidenebisphenol, EDA) are placed in the mono- neck ground flask of 100mL, then, then
1000 μ L 3- isocyanide propyl-triethoxysilicane (3- are drawn with the microsyringe that range is 100 μ of μ L ~ 1000 L
Isocyanatopropyltriethoxysilane, ICPTS) it is added in above-mentioned flask, it is eventually adding 10mL ~ 20mL second
Alcohol, by mixed liquor ultrasonic disperse 7min ~ 9min in above-mentioned 100mL flask, in an inert atmosphere, with 400rpm ~ 600rpm
Mixing speed reacts 5h ~ 7h at 50 DEG C;
The preparation of the titanium dioxide nano-particle of the trace class target molecule of 1.3 surface modification amino and fluorophor: point
Not Liang Qu the ethanol solution of 60mL ~ 80mL and the butyl titanate of 2mL ~ 4mL be placed in ultrasonic mixing in 250mL flask, then
Add the above-mentioned NBD-APTS complex solution prepared, at room temperature with 450rpm ~ 550rpm stirring 2min ~
4min then adds the EDA-ICPTS complex solution prepared, finally, the 500 μ L ammonium hydroxide of μ L ~ 1000 and 440 μ L ~
460 μ L ethyl orthosilicates (Tetraethoxysilane, TEOS) are added in above-mentioned reaction solution, with 700rpm ~ 800rpm
After stirring 3min, speed of agitator is down to 450rpm ~ 550rpm, reacts at room temperature for 24 hours, obtains surface modification amino and fluorescence
The titanium dioxide nano-particle of the trace class target molecule of group, is then mixed with ethyl alcohol with the 50mL that acetone volume ratio is 4:1
Solution elutes class target molecule;
At 90 DEG C, by the titanium dioxide nano-particle of above-mentioned elution class target molecule 60mL concentration be 0.25mol/
Flow back 2h in the tetrahydrofuran solution of the Lithium Aluminium Hydride of L, then cleans removal three times with anhydrous tetrahydro furan and be adsorbed on titanium dioxide
Extra Lithium Aluminium Hydride in nanoparticle surface, obtain containing amino, fluorophor to target molecule have selection identification, detection
Titanium dioxide nano-particle fluorescence probe.
Target molecule is added in the titanium dioxide nano-particle fluorescence probe of surface modification amino, its identification can be changed
Performance.DDT molecule is such as added, amino and the chlorine atom on DDT molecule phenyl ring on nano titania fluorescence probe surface are formed
Hydrogen bond prevents the electronics on the amino rich in electronics from shifting to NBD-Cl, it is suppressed that and fluorescent quenching causes fluorescence enhancement, thus
Obtain the identification and detection to DDT molecule.
Embodiment: first according to covalent coupled reaction, NBD-APTS compound is made, then according to non-covalent bond (hydrogen bond)
The rich amino-containing titanium dioxide nano-particle fluorescence probe in surface can be obtained in reaction and cross-linking reaction.
The first step is the preparation of NBD-APTS compound: firstly, with the chloro- 7- nitre of electronic balance precise 0.0016g 4-
Base benzofuran (4-chloro-7-nitrobenzofurazan, NBD-Cl) is placed in the mono- neck ground flask of 50mL, then, then
220 μ L 3- aminopropyl triethoxysilane (3- are drawn with the microsyringe that range is 100 μ of μ L ~ 1000 L
Aminopropyltriethoxysilane, APTS) it is added in above-mentioned flask, finally, 16mL ethyl alcohol is added into flask again,
By mixture ultrasonic disperse 5min in flask, in an inert atmosphere, 2h is reacted at 50 DEG C with 500 rpm mixing speeds;
Second step is the preparation of EDA-ICPTS compound: first with the sub- second of electronic balance precise 0.4240g 4,4 '-
Base biphenol (4,4 '-Ethylidenebisphenol, EDA) is placed in the mono- neck ground flask of 100mL, then, then with range is
The microsyringe of 100 μ of μ L ~ 1000 L draws 1000 μ L 3- isocyanide propyl-triethoxysilicane (3-
Isocyanatopropyltriethoxysilane, ICPTS) it is added in above-mentioned flask, it is eventually adding 16mL ethyl alcohol, it will be upper
Mixed liquor ultrasonic disperse 8min in 100mL flask is stated, in an inert atmosphere, reacts 6h at 50 DEG C with 500 rpm mixing speeds;
Third step is the system of the titanium dioxide nano-particle of the trace class target molecule of surface modification amino and fluorophor
Standby: the butyl titanate of the ethanol solution and 3mL that measure 70mL respectively is placed in ultrasonic mixing in 250mL flask, then adds
The NBD-APTS complex solution prepared is stated, 3min is stirred with 500rpm at room temperature, then adds the EDA- prepared
ICPTS complex solution, finally, 800 μ L ammonium hydroxide and 440 μ L ethyl orthosilicates (Tetraethoxysilane, TEOS) are added
Into above-mentioned reaction solution, after stirring 3min with 800rpm, speed of agitator is down to 500rpm, is reacted for 24 hours at room temperature, obtains table
The titanium dioxide nano-particle of the trace class target molecule of amino and fluorophor is modified in face, then with ethyl alcohol and acetone volume ratio
Class target molecule is eluted for the 50 mL mixed solutions of 4:1;
At 90 DEG C by the titanium dioxide nano-particle of above-mentioned elution class target molecule 60mL concentration be 0.25mol/L
Lithium Aluminium Hydride tetrahydrofuran solution in flow back 2h, then with anhydrous tetrahydro furan clean removal three times and be adsorbed on titanium dioxide and receive
Extra Lithium Aluminium Hydride on rice corpuscles surface, obtain containing amino, fluorophor to target molecule have selectivity, detection property two
Titanium oxide nanoparticles fluorescence probe.
Claims (5)
1. a kind of preparation method of the titanium dioxide nano-particle fluorescence probe for DDT detection, it is characterised in that: the dioxy
The aminopropyl changed on the print identification site of titanium nanoparticle fluorescence probe interior can be mutual with the DDT molecule into recognition site
It acting on, the chlorine atom on hydrogen atom and DDT molecule on aminopropyl forms hydrogen bond, and stablize aminopropyl, when light excites, prevention ammonia
The electronics transfer of nitrogen-atoms leads to complex fluorescence according to Photo-induced electron transfer mechanism to NBD-APTS compound on propyl
The enhancing of intensity realizes identification and detection to DDT molecule, system by the matching of imprinted sites and the change of fluorescence intensity
Standby process includes following three step:
The preparation of 1.1 NBD-APTS compounds: firstly, with the chloro- 7- of electronic balance precise 0.0010g ~ 0.0030g 4-
Nitrobenzofuran is placed in the mono- neck ground flask of 50 mL, then, then the microsyringe for being 100 μ of μ L ~ 1000 L with range
It draws the 220 μ L 3- aminopropyl triethoxysilanes of μ L ~ 230 to be added in above-mentioned flask, finally, being added 10 into flask again
The mL ethyl alcohol of mL ~ 20, by mixture ultrasonic disperse 4 min ~ 6 min in flask, in an inert atmosphere, with 400 rpm ~
600 rpm mixing speeds react the h of 1 h ~ 3 at 50 DEG C;
The preparation of 1.2 EDA-ICPTS compounds: electronic balance precise 0.4230 g ~ 0.4250 g 4,4 '-is used first
Ethylenebis phenol is placed in the mono- neck ground flask of 100 mL, then, then the micro-sampling for being 100 μ of μ L ~ 1000 L with range
Device is drawn 1000 μ L 3- isocyanide propyl-triethoxysilicanes and is added in above-mentioned flask, and the mL second of 10 mL ~ 20 is eventually adding
Alcohol, by mixed liquor ultrasonic disperse 7 min ~ 9 min in above-mentioned 100 mL flask, in an inert atmosphere, with 400 rpm ~ 600
Rpm mixing speed reacts the h of 5 h ~ 7 at 50 DEG C;
The preparation of the titanium dioxide nano-particle of the trace class target molecule of 1.3 surface modification amino and fluorophor: it measures respectively
The butyl titanate of the ethanol solution and the mL of 2 mL ~ 4 that take the mL of 60 mL ~ 80 is placed in ultrasonic mixing in 250 mL flasks, then
The above-mentioned NBD-APTS complex solution prepared is added, 2 min ~ 4 are stirred with the rpm of 450 rpm ~ 550 at room temperature
Min then adds the EDA-ICPTS complex solution prepared, finally, the 500 μ L ammonium hydroxide of μ L ~ 1000 and 440 μ L
~ 460 μ L ethyl orthosilicates are added in above-mentioned reaction solution, after stirring 3 min with the rpm of 700 rpm ~ 800, speed of agitator
It is down to the rpm of 450 rpm ~ 550, reacts 24 h at room temperature, obtains the trace class target of surface modification amino and fluorophor
The titanium dioxide nano-particle of molecule, the 50 mL mixed solutions elution class target point for being then 4:1 with ethyl alcohol and acetone volume ratio
Son;
At 90 DEG C, by the titanium dioxide nano-particle of above-mentioned elution class target molecule 60 mL concentration be 0.25 mol/L
Lithium Aluminium Hydride tetrahydrofuran solution in flow back 2 h, then clean removal three times with anhydrous tetrahydro furan and be adsorbed on titanium dioxide
Extra Lithium Aluminium Hydride in nanoparticle surface, obtain containing amino, fluorophor to target molecule have selection identification, detection
Titanium dioxide nano-particle fluorescence probe.
2. a kind of preparation method of titanium dioxide nano-particle fluorescence probe for DDT detection according to claim 1,
It is characterized in that: the inert atmosphere refers to nitrogen.
3. a kind of preparation method of titanium dioxide nano-particle fluorescence probe for DDT detection according to claim 1,
It is characterized in that: its partial size of the titanium dioxide nano-particle can be controlled by adjusting the dosage of butyl titanate.
4. a kind of preparation method of titanium dioxide nano-particle fluorescence probe for DDT detection according to claim 1,
It is characterized in that: the class target molecule is 4,4 '-ethylenebis phenol.
5. a kind of preparation method of titanium dioxide nano-particle fluorescence probe for DDT detection according to claim 1,
It is characterized in that: the print identification site inside the fluorescence probe of the titanium dioxide nano-particle is that have and target molecule knot
The void structure of structure, size and function base complementation.
Priority Applications (1)
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